Advanced cellulosic renewable fuels

ABSTRACT

The invention relates to a process to manufacture advanced cellulosic gasolines. Dilute organic acids derived from pyrolized biomass are converted to their corresponding alcohols in a stand-alone hydrodeoxygenation unit followed by membrane pervaporation step to remove water. The alcohol product is blended directly into a neat hydrocarbon fuel basestock to make unadditized gasoline.

CROSS-REFERENCE TO RELATED APPLICATIONS

This Application is a Divisional Patent Application of U.S. Ser. No.13/327,533 filed on Sep. 20, 2011.

FEDERALLY SPONSORED RESEARCH OR DEVELOPMENT

None.

FIELD OF THE INVENTION

This invention relates to a process for the manufacture advancedcellulosic gasoline. In one embodiment of the invention, dilute organicacids derived from biomass are converted to their corresponding alcoholsin a stand-alone hydrodeoxygenation unit followed by a membranepervaporation step to remove water. The alcohol product is blendeddirectly into a neat hydrocarbon fuel basestock to make unadditizedgasoline.

BACKGROUND OF THE INVENTION

The use of renewable energy sources is becoming increasingly necessaryto reduce emissions of carbon based fuels and provide alternatives topetroleum based energy and processing hydrocarbon-based feedstocks. Oneof the process alternatives being explored is the pyrolysis of biomass.Biomass is any carbon containing material derived from living orformerly living organisms, such as wood, wood waste, crops, crop waste,waste, and animal waste.

Biomass can be processed using several techniques. One increasinglypopular technique for processing wood-based feedstocks. Pyrolysis, whichis the thermal decomposition of a substance into its elementalcomponents and/or smaller molecules, is used in various methodsdeveloped for producing hydrocarbons, including but not limited tohydrocarbon fuels, from biomass. Pyrolysis requires moderate to hightemperatures, generally greater than about 325° C., such that the feedmaterial is sufficiently decomposed to produce products which may beused as hydrocarbon building blocks.

Generally the pyrolysis of biomass produces four primary products,namely water, “bio-oil,” also known as “pyrolysis oil,” char, andvarious gases (H₂, CO, CO₂, CH₄, and other light hydrocarbons) that donot condense, except under extreme conditions.

Fast pyrolysis is one method for the conversion of biomass to bio-oilwith high yields. Fast pyrolysis is the rapid thermal decomposition oforganic compounds in the absence of atmospheric or added oxygen toproduce liquids, char, and gas. Generally, fast pyrolysis uses dry (<10%moisture) feedstock of biomass comminuted into small particles (<about 3mm), moderate temperatures (325-750° C.), and short residence times(0.5-2 seconds). This pyrolysis reaction may be followed by rapidquenching to avoid further decomposition of the pyrolysis products andsecondary reactions amongst the pyrolysis products.

Fast pyrolysis affords operation at atmospheric pressure, moderatelyhigh temperatures, and with low or no water usage. Bio-oil yieldstypically range from 50-75% the mass of input biomass and are heavilyfeedstock dependent. Generally, known methods of bio-oil productionresult in bio-oil with high oxygen (>50 wt %) and water content (>30%);such oxygen and water content may result in storage instability andphase-separation issues.

For example, the pyrolysis of a wood based biomass will produce amixture of organic compounds such as lignin fragments, aldehydes,carboxylic acids, phenols, furfurals, alcohols, and ketones, as well aswater. Unfortunately, compounds such as the aldehydes and acids mayreact with other components of the bio-oil, creating instability,corrosiveness, and poor combustion characteristics.

Bio-oil typically requires additional upgrading in the presence of acatalyst and/or hydrogen to be used in transportation fuel applications.These upgrading steps can be integrated into the existing pyrolysis unitor used in post-treatment schemes. Shabtai, et al., U.S. Pat. No.5,959,167, use a catalytic reaction process to produce a reformulatedhydrocarbon gasoline product. Marker and Petri, U.S. Pat. No. 7,578,927,convert pyrolytic lignin material into naphtha and diesel boiling rangecomponents, having low acidity and ultra-low sulfur content. Zmierczakand Miller, US2008050792, use a base catalyzed depolymerization (BCD)reaction to produce a partially depolymerized lignin for furtherprocessing to fuel range products. Baldiraghi and associates,WO2008113492, describes a process using hydrodeoxygenation followed byhydroisomerization on an acidic SiO₂/Al₂O₃ catalyst. Bzdek andPellegrino, US2008092435, provide biodiesel fuels prepared by removingdeleterious chemical species from the fuel to insure the filterabilityof the fuel, both neat and in various biodiesel fuel blends. Kleinert,et al. (2009), convert lignin residues from lignocellulosic ethanolproduction into organic liquids with a high hydrogen to carbon (H/C) anda very low oxygen to carbon (O/C) ratio.

Upgrading pyrolysis oils is difficult due to acidity of the pyrolysisoil, contamination with other compounds, and the tendency to form cokeby-products. Damaging costly cracking catalysts is expensive and removesany profit margins from processing biomass and pyrolysis oil to highvalue hydrocarbons. Therefore, it would be desirable to have a method ofcracking biomass, decreasing acidity by removing the organic acids andupgrading pyrolysis oil into useful products in a cost effective manner.

BRIEF SUMMARY OF THE DISCLOSURE

In one embodiment, a process to manufacture advanced cellulosic gasolineis described. Dilute organic acids derived from pyrolized biomass areconverted to their corresponding alcohols in a stand-alonehydrodeoxygenation unit followed by membrane pervaporation step toremove water. The alcohol product is blended directly into a neathydrocarbon fuel basestock to make unadditized gasoline.

In one embodiment, a system for producing a renewable gasoline fromcellulosic biomass is described where a cellulosic feedstream isseparated via an ionic separator (ISEP) into a sugar/polyol stream and awater/carboxylate stream. The polyol stream system is hydrotreated togenerate hydrocarbons from sugars and polyols, and isomerized (ISOM) togenerate isomerized gasoline range hydrocarbons. The carboxylate streamsystem is hydrodeoxygenated (HDO) generating gasoline from thecarboxylate stream and hydrogen. A portion of the hydrocarbon stream, iscold separated to separate alcohols, water, and hydrogen, and a membraneseparated to remove water from alcohol. The gasoline range hydrocarbonsare mixed with alcohols to produce a renewable gasoline.

In another embodiment, a method for producing a renewable gasoline fromcellulosic biomass where a cellulosic feedstream is separated using anionic separator (ISEP) to generate a sugar/polyol stream and awater/carboxylate stream. Hydrocarbons are generated from the sugars andpolyols using a hydrotreating (HT) reactor and converting thehydrocarbons to isomerized gasoline range hydrocarbons using anisomerization (ISOM) reactor. Alcohols are generated from thecarboxylate stream (b), hydrocarbons (i) and recycled hydrogen in ahydrodeoxygenation (HDO) reactor. Alcohol, water, and hydrogen areseparated using a cold separator, and water is removed using a membraneseparator. Product streams are produced comprising alcohol and gasolinerange hydrocarbons.

In another embodiment, a renewable gasoline is produced from cellulosicbiomass by feeding a cellulosic feedstream; using a separator (ISEP) togenerate a polyol stream and a water/carboxylate stream: generatinghydrocarbons from polyols using a hydrodesulfurization (HDS) reactor andconverting the hydrocarbons to isomerized gasoline range hydrocarbonsusing an isomerization (ISOM) reactor; generating alcohol from thecarboxylate stream (b), hydrocarbons (i) and recycled hydrogen in ahydrodeoxygenation (HDO) reactor, separating alcohol, water, andhydrogen using a cold separator, and removing water using a membraneseparator; and producing a renewable gasoline by blending alcohol andgasoline range hydrocarbons.

The renewable gasoline may be a premium, E10, E20, E85, or other blendedgasoline product. The HDO reactor may contain CuO, ZnO, Fe₂O₃, CuO/ZnO,CuO/Fe₂O₃, ZnO/Fe₂O₃, CuO/ZnO/Fe₂O₃, CuO/ZnO/Al₂O₃, CuO/Al₂O₃/SiO₂,CuO/Fe₂O₃/Al₂O₃/SiO₂, catalysts and combinations of those catalysts. Thepervaporation membrane may have a hydrophilic, hydrophobic,organophillic, polydimethylsiloxane (PDMS), polyvinyl alcohol (PVA),polyimide, ceramic, zeolite, amorphous silica, hybrid membranes, orcombinations of membranes.

BRIEF DESCRIPTION OF THE DRAWINGS

A more complete understanding of the present invention and benefitsthereof may be acquired by referring to the follow description taken inconjunction with the accompanying drawings in which:

FIG. 1: Overview of the Advanced Cellulosic Gasoline Process.

FIG. 2: Pyrolysis Oil Advanced Cellulosic Gasoline Process

FIG. 3: Representative plot of % conversion of acetic acid and yield toethanol vs. time on stream for a high conversion run. These data werecollected at 325° C., 400 psig, LHSV=7.5 h⁻¹.

FIG. 4: Equilibrium limited yield of ethanol and acetaldehyde as afunction of temperature at constant pressure (P=250 psig), H₂:HC=50:1,and H₂O:HC=28:1.

FIG. 5: Equilibrium limited yield of ethanol and acetaldehyde as afunction of pressure at constant temperature (T=300° C.), H₂:HC=50:1,and H₂O:HC=28:1.

FIG. 6: Saturation pressure of pure acetic acid vs. temperature. Thebold line is at T=275° C. for reference.

FIG. 7: (a) Equilibrium limited yield of ethanol and acetaldehyde as afunction of water content of feed at constant temperature and pressure(T=300° C., P=250 psig, H₂:HC=50.) (b) Equilibrium limited yield ofethanol and acetaldehyde as a function of hydrogen to acetic acid ratioat constant temperature and pressure (T=300° C., P=250 psig, H₂O:HC=28.)(c) Same conditions as (b), but H₂O:HC=9.3.

FIG. 8: Schematics of a pervaporation membrane. A) A pervaporationmembrane with an ethanol/water feed. B) The pervaporation membraneincluding 500 ml reservoir with thermostat, feed stream, returnregulation valve, concentrate, permeate and a vacuum pump.

FIG. 9: A) Trend in water flux as a function of time. Feed:Ethanol/water (90/10 wt %) mixture at 80° C. B) Concentration of waterin feed as a function of time.

FIG. 10: A) Concentration of ethanol in permeate as a function of time.B) Water flux is plotted as a function of the driving force. The slopeof the trend line gives the permeance across the membrane. The fugacity(Pa) of water in the feed is highest at the start of the experiment anddecreases as the experiment proceeds (from the right to the left on Xaxis). Note: Runs 1-5 have been plotted with the same symbol to describea linear overall trend.

FIG. 11: A) Ethanol flux is plotted as a function of the fugacity ofethanol in feed. The fugacity of ethanol in the feed is lowest at thestart of the experiment and increases as the experiment proceeds (fromthe left to the right on X axis). B) Effect of fugacity of water in feedon ethanol flux. The fugacity of water in the feed is highest at thestart of the experiment and decreases as the experiment proceeds (fromthe right to the left on X axis).

FIG. 12: Selectivity of water over ethanol as a function of waterconcentration in feed.

DETAILED DESCRIPTION

Turning now to the detailed description of the preferred arrangement orarrangements of the present invention, it should be understood that theinventive features and concepts may be manifested in other arrangementsand that the scope of the invention is not limited to the embodimentsdescribed or illustrated. The scope of the invention is intended only tobe limited by the scope of the claims that follow.

The pyrolysis method of upgrading biomass into motor fuel feedstocksproduces aqueous streams containing roughly 50% of the total carboncontent of the original substrate. Light organic acids (eg. formic,acetic, and propanoic acid) make up 20% of the carbonaceous species inthis waste stream. Another sizable portion of this aqueous carbon iscontained in various sugar molecules. The corrosive nature and high acidcontent of the stream prohibits many traditional upgrading routes, yetas it is a reasonable amount of the pyrolysis product, it is desirableto seek methods of converting the stream into products. Any renewablefuel product from the conversion of the acids in the aqueous streamcould potentially fall into the category of an “Advanced Biofuel” or“Cellulosic Biofuel” assuming the reduction of baseline greenhouse gasemissions requirement is met. (The Advanced Biofuel classificationrequires a 50% reduction of the baseline lifecycle greenhouse gasemissions (BLGGE) of the new fuel over that being replaced, andCellulosic requires a 60% reduction.)

Hydrodeoxygenation (HDO) of the acids to the corresponding alcohols anddecarbonylation or dehydration of these alcohols to gaseous products aretechniques use to upgrade bio-oil to hydrocarbon fuels. Aspects of thesetechniques are advantageous and disadvantageous. HDO of the acids toalcohols yields products which have appealing physical properties fordirect blending into motor fuels (eg. ethanol, propanol, etc.) However,the process consumes a substantial amount of hydrogen which couldprohibit the classification of the product as a Cellulosic or AdvancedBiofuel. The CO₂ footprint of the fuel could be reduced if a low-CO₂ orCO₂-free H₂ source is used leaving this as a viable option forupgrading. Assuming the greenhouse qualification is met, this couldpotentially compete with cellulosic ethanol, a highly discussed productbeing explored by other groups in the field which is produced by thefermentation of carbohydrates obtained by acid hydrolysis of cellulose.

In one embodiment, dilute stream of ogranic acids is converted tooxygenated gasoline blending components in high yields thus eliminatingthe need for traditional evaporators and distillation columns. Theprocess involves three main steps (in the following ordered sequence):1.) HDO of the dilute organic acid feedstream to alcohol followed by 2)Membrane separation of the produced water in step 1. and 3) co-blendingwith hydrocarbons to form the final fuel product. Additionalhydrocarbons used in the final blending step can come from the sugars inthe original waste stream and/or any other source of neat hydrocarbons.Therefore, the final blend can be partially or completely renewable. Anexample is illustrated in the attached FIG. 1. Here, dilute acetic acidproduced from the pyrolysis of corn fiber is separated from the sugarfraction. Hydrogen is added to this stream. It is then preheated andsent to the HDO unit operating at very high yields and completeconversion of the organic acid. The resulting product stream consistingof mainly ethanol, water, H₂, with small amounts of ethyl acetate issent to a high pressure, cold separator to remove some of the water andflash-off the hydrogen-rich light-gases for recyling. The remaininghydrous stream rich ethanol is sent to a pervaporation unit containing ahydrophilic material to completely separate out the water. Theconcentrated ethanol stream is blended with hydrocarbons and sentdirectly to storage as unadditized E85 or blended with sugar-alcoholderived hexane isomers to make unadditized E10 or E20 gasoline.

Dilute, “waste” organic acid streams are converted in a HDO reactorloaded with a novel catalyst that requires no sulfiding pre-treatment orsulfiding agents, and works at mild temperatures <600° F. and lower H₂pressures, <800 psig. The water is removed from the product stream usingpervaporation technology. So, there is no need for high temperature,azeotropic, molecular sieve based fractionation. A final membraneseparation step allows for the alcohol product stream to be “ready forfuel blending” by drying and removing any remaining water.

Dilute organic acid streams may be any biologically derived organic acidstream including, but not limited to, natural fermentation products,pyrolysis products, and other sources of biological acids. Cellulosicpyrolysis product as used herein may be pyrolysis product from anynatural biological source including but not limited to plant materials,cellulosic biomass, wood pulp, waste paper products, wood chips, cottonbyproducts, cotton wastes, corn fibers, grasses, cellodextrins,polysaccharides, hemp, switchgrass, Miscanthus, Salix (willow), andPopulus (poplar), as well as lignins, insoluble starches, glycogens, andother biological solids.

Hydrodeoxygenation catalyst as used herein includes a copper (Cu) oriron (Fe) catalyst that catalyzes the reduction of carboxyl functionalgroups in organic acids. In one embodiment, a supported CuO catalyst isused that may include any solid support with CuO precipitated. The CuOcatalyst may contain a promoter or additional catalytic metals. In oneembodiment, a bulk CuO/ZnO/Al₂O₃ syn-gas conversion catalyst is used. Inanother embodiment, a Fe₂O₃ catalyst is used including but not limitedto CuO/Fe₂O₃/Al₂O₃/SiO₂. Other catalysts may also be available thatselectively reduce carboxyl functions in organic acids to producehydroxyl functions in alcohols.

Organic acids may include acetic acid, propionic acid, butyric acid andthe like.

In one embodiment' the membrane cell contains (i) sintered disk, (ii)fleece, (iii) flat sheet membrane, and (iv) O-ring.

The fundamental equations governing the pervaporation mechanism aredetailed below. The flux of component i across the membrane is given bythe relation:

$\begin{matrix}{J_{i} = {\frac{P_{m}^{i}}{l}\left\lbrack {f_{i}^{L} - f_{i}^{P}} \right\rbrack}} & (1)\end{matrix}$

Where (P_(m) ^(i)/l ) is permeance across the membrane. The drivingforce in pervaporation is the fugacity difference across the membrane,i.e., the difference in the fugacity of the liquid feed (ƒ_(i) ^(L)) andthe permeate in the vapor form (ƒ_(i) ^(P)). Therefore, from Eq. 1 weget:Flux=Permeance·Driving Force

For the sake of simplicity, a high vacuum is assumed to be applied onthe permeate side rendering the fugacity of the permeate (ƒ_(i) ^(P))insignificant in comparison to the fugacity of the feed. Hence, ƒ_(i)^(P) tends to zero. Eq. 1 can thus be simplified to:

$\begin{matrix}{J_{i} = {\frac{P_{m}^{i}}{l}\left\lbrack f_{i}^{L} \right\rbrack}} & (2)\end{matrix}$

In pervaporation, the fugacity of the liquid feed inclusive of all thenon-ideality effects is given by the relation:

$\begin{matrix}{f_{i}^{L} = {\gamma_{i}x_{i}\phi_{i}^{sat}P_{i}^{sat}{\exp\left\lbrack \frac{\int_{P_{i}^{sat}}^{P}{V_{i}\ {\mathbb{d}P}}}{RT} \right\rbrack}}} & (3)\end{matrix}$

The exponential term in Eq. 3 is known as the Poynting correctionfactor. For temperatures quite less than the critical temperature thevariation in the liquid phase molar volume (V_(i)) with pressure isnegligible.3 Calculating V_(i) at saturation condition gives thegeneralized form of fugacity:

$\begin{matrix}{f_{i}^{L} = {\gamma_{i}x_{i}\phi_{i}^{sat}P_{i}^{sat}{\exp\left\lbrack \frac{V_{i}^{sat}\left( {P - P_{i}^{sat}} \right)}{RT} \right\rbrack}}} & (4)\end{matrix}$

The activity coefficient (y) is calculated from Gibbs free energy modelslike NRTL-RK for the corresponding feed composition and temperature. Theoperating feed pressures for pervaporation are low enough to assumeideal gas behavior. The feed pressure (P) in Eq. 4 is typically close toatmospheric pressure. As a result, the fugacity coefficient term (φ_(i)^(sat)) can be approximated as equal to 1. Also, the Poynting correctionfactor is significantly different from 1 only if the pressuredifferential (Eq. 4) is high. As an example, for water, Poyntingcorrection factor is 1.007 for a pressure differential of 10 atmTherefore, for pervaporation the exponential term can be regarded asequal to 1.

The simplified form of fugacity equation is as follows:ƒ_(i) ^(L)=γ_(i)x_(i)P_(i) ^(sat)  (5)

Where the vapor pressure is obtained using the Antoine Equation at thefeed temperature while the mole fraction (x_(i)) is calculated from acomposition analysis of the feed using a Gas Chromatograph. The flux isobtained from the amount of permeate collected across the membrane in astipulated time. Thus, a pervaporation experiment provides the flux ofthe component though the membrane and the compositions of the feed andpermeate.

Substituting the experimentally derived values in Eq. 2 & 5, thepermeability of species i is given by:

$\begin{matrix}{P_{m}^{i} = \frac{J_{i}l}{\gamma_{i}x_{i}P_{i}^{sat}}} & (6)\end{matrix}$

Selectivity (α_(i/j)) of component i is calculated from the feed andpermeate concentrations by the following relation:

$\begin{matrix}{\alpha_{i/j} = \frac{\left( {y_{i}/y_{j}} \right)}{\left( {x_{i}/x_{j}} \right)}} & (7)\end{matrix}$

Selectivity, in a pervaporation process, is a combination of therelative volatility (α_(VLE)) of the species and the intrinsic membraneselectivity (α₀) as shown by the following relation:α_(i/j)=α_(VLE).α₀  (8)

The key variables to ascertain membrane performance, i.e., permeabilityand selectivity can thus be determined experimentally.

The maximum permeate pressure to achieve separation is given by thefugacity of the permeating components on the feed side. If the fugacityon the permeate side becomes higher than or equal to the one on the feedside, then there will be no flux. For industrial scale operation, highvacuum levels obtained at lab-scale may not be achievable. This can becompensated by increasing the membrane area. Also, for commercialmembranes the selective layer of membrane is relatively thinner (1-2microns) resulting in higher flux.

Pervaporation Membrane as used herein is a membrane or membrane systemthat can be used to perform pervaporation to separate water andalcohols. Pervaporation is a process that facilitates the separation oftwo or more species via simultaneous porous diffusion and evaporation.The membrane material is selected to maximize the separation requiredand different pervaporation membranes may be used for differentsepartations. A hydrophilic membrane is used for dehydration of organicsolvents. A hydrophobic membrane is used for the removal of volatileorganics. An organophilic membrane is used for the separation ofaromatics hydrocarbons from aliphatics. The membrane material can bealtered to obtain the right combination of flux and selectivity.Numerous hydrophobic membranes are available includingpolydimethylsiloxane (PDMS). Hydrophilic membranes including polyvinylalcohol (PVA), polyimide, ceramic, zeolite, and other membranes withhydrophilic properties. In addition to ceramic membranes, amorphoussilica membranes have been manufactured using sol-gel chemical processesto tailor membrane selectivity. Hybrid membranes includingorganic-inorganic hybrids may also be used to further tailorpervaporation selectivity. Membranes may be supported membranes orhollow fiber membranes. HYBSI® hybrid silica membranes may be used underhydrothermal and/or acidic conditions. The Pervap 2200® is a hydrophilicPVA membrane with a polyacrylonitrile (PAN) support used to separatewater from organics. A variety of membranes are available fromPERVATECH™, SULZER™, Jiangsu Jiuwu High-Tech Co., Ltd., King MembraneEnergy Technology Inc., Fortune International Tech Materials Inc., andothers, including thin film membranes described in WO/2010/145901,poly(1-trimethylsilyl-1-propyne) (PTMSP) membranes and otherpervaporation membranes. Because membranes are selected based on theproperties of the retentate and permeate, it is possible to select oneor more membranes for a separation dependent upon the system,temperatures, flux, and other properties, to achieve a high level ofseparation.

Feed composition as described herein is the mixture of two or morecomponents in a feedstock. Feedstocks may include a variety ofoxygenates, organic acids, polyols, alcohols, hydrocarbons, water,salts, and byproducts found in pyrolysis oil, HDO intermediates and HDOproducts. The composition influences the membrane performance and typeof membrane chosen. The selectivity of a membrane decreases as thenumber of components in the feed mixture increase and is affected by theconcentrations of those components. Although some examples are providedthere is a wide range of feed compositions that cannot be enumeratedhere. The feed composition will typically be raw feed stream producedfrom the HDO reaction that may or may not be processed to removecontaminants.

The feed stream may contain any concentration of alcohol and water alongwith other contaminants, intermediates and byproducts. The feed streammay contain anywhere from 1 to 99% alcohol and inversely may containanywhere from 99 to 1% water. In one embodiment, the feed streamcomprises 90% ethanol and 10% water. In another embodiment the feedstream comprises approximately 1:9 alcohol:water; approximately 2:8alcohol:water; approximately 3:7 alcohol:water; approximately 4:6alcohol:water; approximately 5:5 alcohol:water; approximately 6:4alcohol:water; approximately 7:3 alcohol:water; approximately 8:2alcohol:water or approximately 9:1 alcohol:water. The ratio of alcoholto water may be controlled for the purpose of making model preparationsand baseline testing, but the raw feed from the HDO may have a varietyof alcohol, water and contaminant concentrations that are affected bythe amount of water in the biological feed stream, water added duringprocessing and water separated using other methods. Thus thepervaporation feed stream may have an unknown concentration of alcohol,water and other byproducts.

In order to maximize permability, if the alcohol concentration is above50%, a hydrophilic membrane may be used making water the permeate andalcohol the retentate. Feed streams may be subjected to one or moremembrane pervaporations to increase alcohol concentrations. Finalconcentrations for dried alcohol may have less than 0.1 wt % water.

Feed temperature as used herein is the temperature of the feed stream.In pervaporation, it is desired to have the feed temperature as high aspossible to increase the vapor pressure of the components. This istypically determined by the maximum temperature at which the membrane isstable. In one embodiment a PVA membrane is stable to about 100° C., butmay increase or decrease in various feed stream compositions,preparation and/or treatment of the membrane, and/or source of themembrane. In another embodiment feed temperature is 80° C. Feedtemperatures may range from slightly above water's freezing point tonear boiling and are dependent upon the feed composition, temperatureand pressure of the system. Feed temperatures may be betweenapproximately 0° C. and approximately 120° C., including approximately10° C., 20° C., 30° C., 40° C., 50° C., 60° C., 70° C., 80° C., 90° C.,100° C., to about 110° C. Although some examples are provided there is awide range of feed temperatures that cannot be enumerated here. The feedtemperatures may simply be the temperature at which the alcohol/watermixture is produced from the previous production step.

Feed flow rate as used herein is the volumetric rate of fluid flow ofthe feed stream. The flow rate is kept at maximum rate such that theentire membrane area experiences the same temperature and concentrationof feed. In one embodiment, the flow rate is maintained at 140liters/hr.

Permeate pressure as described herein is the pressure on the permeateside of the membrane. The permeate pressure is less than thefeed/retentate pressure to drive permeate across the membrane. To obtainflux, the permeate pressure should be lower than the vapor pressure ofthe component to be separated. In one embodiment, the permeate pressureis kept as low as possible to allow the maximum driving force forseparation (Eq. 1 & 2). In one embodiment, the vacuum on the permeateside is maintained at approximately 3 mbar.

The following examples of certain embodiments of the invention aregiven. Each example is provided by way of explanation of the invention,one of many embodiments of the invention, and the following examplesshould not be read to limit, or define, the scope of the invention.

Example 1 HDO

Light organic acids compose a major portion of the pyrolysis oil (up to10 wt %) product used for producing biofuels. These organic acidsgenerally appear in low concentrations within the aqueous fractions ofthe pyrolysis oil. Reconstitution of pyrolysis oil from essentiallythese aqueous waste streams into biofuels is accomplished by HDO. HDOproduces alcohols from this organic acids which may be directly blendedinto conventional fuels. Several catalysts were identified and examinedfor their relative activity in converting a model stream of acetic acidto ethanol. One catalyst (CuO/ZnO/Al₂O₃) was selected to carry-out HDO,and a matrix of designed experiments were performed to model theconversion over a range of conditions. CuO/ZnO/Al₂O₃ produced a varietyof products at high conversion (94% conversion), and a high yield, 75%,of ethanol.

CuO/ZnO/Al₂O₃ synthesis gas conversion catalyst with a MgO promoter wasprepared via coprecipitation (nominally 67.3% CuO, 22.8% ZnO, 8.9%Al₂O₃, 1.0% MgO). A solution containing the desired ratio of coppernitrate, zinc nitrate, aluminum nitrate, and magnesium nitrate wasprecipitated at a pH of 9.5 using a 2 molar sodium carbonate solution tomaintain pH. The solution was digested at 70° C. for 60 minutes undercontinuous stirring. Samples were filtered and washed with DI water,dried, and calcined at 350° C. for 6 hours. Catalyst was sieved to−40/+100 mesh. Catalyst samples were reduced at 300° C. prior to use.

CuO/Fe₂O₃/Al₂O₃/SiO₂ was prepared by the incipient wetness techniqueusing dried silica as a support (5% CuO, 50% Fe₂O₃, 10% Al₂O₃, 35%SiO₂). Al₂O₃ was loaded first onto the support by dissolving the desiredamount of aluminum nitrate in the volume of water which the particleswere capable of absorbing. The catalyst was dried overnight and calcinedat 635° C. for 2 hours. Iron citrate and copper nitrate were then addedto the catalyst in the desired loadings using the same method. The finalcatalysts were again dried and calcined at 635° C. for 2 hours. Catalystsamples were reduced at 480° C. in pure H₂ prior to use. CuO/Al₂O₃/SiO₂was prepared similarly, but without the addition of iron (5% CuO, 10%Al₂O₃, 85% SiO₂).

Catalytic data were acquired using a ½″, downflow reactor. An alundumbed was used above the catalyst bed to assist in flashing the feed toreaction temperature prior to contacting the catalyst. Catalysts werediluted in alundum to a constant bed volume. The reactor was heatedusing a three-zone furnace with independent temperature control for eachzone. Gaseous carriers and reagents were delivered using mass flowcontrollers. Liquid feed was delivered to the system by a high-pressuresyringe pump. The system pressure was controlled by a backpressureregulator.

Catalysts were reduced in-situ for 2 hours in 500 sccm H₂ at 400 psigprior to each run at the temperatures specified earlier. Runs wereperformed at a constant liquid feed rate of 15 mL/hr, using a nominally10.4 wt % acetic acid in water feed. The H₂:HC ratio was 51.5, and theH₂O:HC was 28.8 for all HDO runs.

The corrosive nature and high acid content of the aqueous pyrolysis oilproducts prohibit many traditional upgrading routes. These propertiesalso limit the catalysts that may be used in its upgrading as many aremetal oxides which would be dissolved in the passing liquid organicacid. The simplest method of mitigating the corrosiveness of the feed isto flash it off prior to contacting it with the catalyst. Whileenergetically demanding, this method was found to be effective inallowing the use of several catalysts which readily dissolve in theaqueous liquid acid even at room temperature (e.g. CuO/ZnO/MgO/Al₂O₃.)

The conversion of organic acids to alcohols via HDO is astraight-forward approach for upgrading to transportation fuels. Threecatalysts were selected for examining the conversion of aqueous aceticacid to ethanol.

TABLE 3 Comparison of Catalysts for HDO Activity⁽¹⁾ Catalyst %Conversion % Selectivity⁽²⁾ CuO/ZnO/Al₂O₃ ⁽³⁾ 94.2% 76.2% CuO/Al₂O₃/SiO₂  <1%   ~0% CuO/Fe₂O₃/Al₂O₃/SiO₂  5.8% 17.5% ⁽¹⁾Reactions at 350° C.,400 psig, and 7.5 h⁻¹ LHSV. ⁽²⁾Selectivities are given to ethanol.⁽³⁾CuO/ZnO/Al₂O₃ reaction at 325° C. to reduce the possibility ofsintering.

Results from the catalysts examined are presented in Table 3. TheCuO/ZnO/Al₂O₃ catalyst produced the highest yield of ethanol, followedby significant yields of light gases and smaller amounts of methanol,ethyl acetate, and acetone. CuO/Fe₂O₃/Al₂O₃/SiO₂ exhibited a lower levelof conversion. CuO/Al₂O₃/SiO₂ exhibited almost no ethanol conversion.The formation of acetone by the CuO/ZnO/Al₂O₃ sample may be explained bythe following reactions 1, 2, and 3 (below). Given this fact, it issomewhat surprising that the supported

CuO/Fe₂O₃/Al₂O₃/SiO₂ did not produce any appreciable amount of acetonenor CO₂.

FIGS. 4 and 5 illustrate how the equilibrium yield of ethanol andacetaldehyde are affected by changing individual run conditions. Astemperature is increased, ethanol's limited yield decreases due to thepositive entropy of the reaction. Increasing pressure increases thelimited yield due to LeChatlier's Principle as the Δn_(gas) for theoverall reaction (acetic acidΔacetaldehydeΔethanol) is −1. It isimportant to point out that while it seems that increasing the pressureand decreasing the temperature would be the optimum way of convertingthe stream (assuming a catalyst was available to reach equilibrium), onemust also be cognizant of the liquid-vapor phase transition along theP-T curve. As mentioned previously, condensing the acid in the catalystbed would result in dissolution of the media. FIG. 6 contains thesaturation pressure for acetic acid as a function of temperature. Fromthe diagram, operation at 275° C. has a saturation pressure just above400 psig.

Model streams of acetic acid representing the aqueous organic acidstream produced during the conversion of biomass to pyrolysis oil may beupgraded to gasoline range alcohols (conversion=94%, yield alcohols=72%,LHSV=7.5 h⁻¹, P=400 psig, T=325° C.). HDO's alcohol products competedirectly with cellulosic ethanol given renewable H₂ and heating sources.If high H₂/HC ratios limit increase costs due to compression of thehydrogen, concentration of the acetic acid feedstream is astraight-forward method of reducing the hydrogen requirement.

Example 2 Pervaporation Membrane Unit

Pervaporation is a membrane-based technique used for separation ofliquid mixtures and in particular for challenging separation ofazeotropes and close-boiling components. For example, binary mixtures ofwater and ethanol form an azeotrope at 95% ethanol. With the anticipatedneed for reducing the carbon footprint in an operation, pervaporationcan provide an alternative to certain distillation steps thus makingrefinery operations more energy efficient. A pervaporation membranetesting unit (FIG. 8B) and its validation using commercial membranes isdescribed. It illustrates the basics of pervaporation, the experimentalprocedure and analysis required to assess membrane performance. In oneembodiment, 80% of the water is removed from a 90/10 wt % ethanol/watermixture using a hydrophilic (SULZER PERVAP2200®) membrane. In additionto 90/10 ethanol/water separation, commercial grade pervaporationsystems can be used to separate hydrocarbon mixtures on a commercialscale. These membrane-based refinery configurations decrease CO₂emissions.

A pervaporation membrane unit has been developed that can processalcohol/water solutions to selectively separate alcohol from water (FIG.8). In one example, an ethanol/water (90/10) wt % mixture was separatedusing a SULZER PERVAP2200® membrane. The process shows goodreproducibility with sufficient scalability. Regression analysis showsthat the data is within 95% confidence limits (FIG. 10B) with an errorof ±4.68 mole/m² hr in the prediction of water flux. Waterpreferentially permeated through the hydrophilic SULZER polyvinylalcohol membrane with a selectivity of 200-450 depending on the waterconcentration in the feed. The average flux of 0.62 kg/m² hr and ethanolloss of 3.5% obtained experimentally were within standard operatinglosses for pervaporation membranes. Flux versus fugacity data shows alinear trend and follows the theory of pervaporation (Eq. 2) allowingfor extrapolation to design level of water concentration withconfidence. This facilitates the calculation of a single value forpermeability of water (˜6.8×10−9 mole/m hr Pa) through the membrane.

The pervaporation experiments are carried out on a lab-scale unitmanufactured by SULZER Chemtech. A schematic and photograph of the unitare shown in FIG. 8B. The stainless steel units used in the experimentsare suitable to handle hydrocarbon mixtures. The feed is introduced viaa centrifugal pump from a 2 liter capacity, heated storage tank across avertically aligned flat sheet membrane (effective area of 165 cm²). Thepermeate vapors drawn via a vacuum pump are collected in two glasscondensers placed in series. The condensers are placed in dewars filledwith liquid N₂ to ensure complete condensation of the permeate vapors.The membrane cell is arranged with a sintered disk, fleece sheet (toprotect the membrane), membrane (with the selective layer facing thefeed) and an O-ring (to have a good vacuum seal). The membrane cell ismounted vertically, in one configuration, but dependent upon the feedstream, surface area and membrane cell geometry, the system may beassembled in various orientations. Commercial membrane cells may bemanufactured with a variety of configurations that depend upon both themembrane design and the process design.

In one embodiment an ethanol/water (90/10 wt %) feed at 80° C. isseparated using a hydrophilic membrane (SULZER PERVAP 2200®). Themembrane has a polyvinyl alcohol (PVA) selective layer (˜4 micron thick)on a polyacrylonitrile (PAN) support (70-100 microns). In oneembodiment, a hydrophilic membrane is fed a 90/10 wt % ethanol/waterfeed composition at 100° C., with a 140 liter/hr flow rate, permeatepressure is maintained at 3 mbar. Conditions are maintained at constantto gauge the experimental errors and repeatability of membraneperformance. Other conditions like feed temperature, flow rate andpermeate pressure may adjust to changes in membrane type, feedstockcomposition or flux rate .

Start up is initiated to prepare the system for pervaporation. Themembrane unit with the condensers is arranged as shown in FIG. 8B. Feedis circulated until the desired temperature is reached. A sample of thefeed is taken prior to pervaporation. A sample of the permeatecondensate is also taken. These are permeate vapors which are condensedvia liquid N₂ on the product side.

During pervaporation the system is allowed to run at the steady-statefeed temperature. Feed samples are collected after a period of time onstream. For commercial membranes with a thin selective layer (˜1-4microns), the time required to achieve concentration stabilization maybe less (on the order of a few minutes). For the next interval, morefeed is collected. This will be the first feed sample after achievingsteady-state at the required temperature. The concentration of feed usedfor the second interval will be based on the moving average of previoustime intervals to account for any feed concentration variation in abatch process. The condensers are weighed after reaching roomtemperature to calculate the mass of permeate collected. The mass ofpermeate divided by the membrane area and time interval gives the totalflux across the membrane. Feed and permeate samples are analyzed in agas chromatograph (GC) to determine their respective concentrations.Selectivity across the membrane may be calculated using Eq. 7. Samplesmay be collected at 1-hour time intervals through a given period. Thefeed is typically changed for a repeat run the next time period (24 hr,8 hr, or other time period). The runs are repeated until the curves offlux versus average concentration data coincide.

FIG. 9A shows a gradual decrease in water flux over the duration of thebatch experiment. This result follows directly from Eq. 2, as watercontinues to permeate through the membrane, the water concentration inthe feed should decrease correspondingly. This decreases the fugacity orthe driving force for pervaporation. Hence, there is a drop in the waterflux over time. This observation is further confirmed by the GC analysisof the feed water at various intervals during the experiment. FIG. 9B, aplot of water concentration versus time, shows a 40% drop in waterconcentration from 10% to 6% in feed during an 8 hour run and subsequentdrop to 4% during an extended run (Run 5). This shows that thehydrophilic PVA membrane is applicable for water permeation. Incontrast, ethanol gets enriched in the feed that is re-circulated.Analysis of the permeate (FIG. 10A) shows a small loss of ethanol (<5%)into the permeate stream.

In pervaporation, the flux of a component increases with its fugacity ordriving force (Eq. 2). Water flux is a linear function of the fugacityof water in feed (FIG. 10). The slope of the line gives the permeance ofwater (˜1.7×10⁻³ mole/m² hr Pa). Permeance multiplied by the membranethickness (thickness of selective layer) gives the correspondingpermeability value. For a membrane thickness of 4 microns, thepermeability of water at the given conditions is ˜6.8×10⁻⁹ mole/m² hrPa. The data can be fitted to a straight line with an R-squared value of0.84. This shows good repeatability of the data within the experimentalerror. The scatter in the flux versus fugacity data is typical forpervaporation experiments performed previously with water. Regressionanalysis shows that the experimental data is within the 95% confidencelimits with a cumulative error of ±4.68 mole/m² hr in predicting thevalue of water flux.

TABLE 4 Comparison of COP and SULZER pervaporation membrane performancedata. Values expressed are average values for ethanol/water (90/10) wt %mixture at 80° C. Pervaporation Expected Total Flux (kg/m² · hr) 0.620.45 Ethanol Loss (wt %) 3.5% <5%

The flux and ethanol loss values observed in Table 4 are better than theexpected values calculated from the flux model in Eq. 2. The dataobtained shows a higher flux and a corresponding lower ethanol loss intothe permeate. Given the variables associated with the experiment (e.g.uniform feed temperature, high vacuum on permeate side etc) and thepropagation of errors, the results obtained are statistically equivalentwith the expected values.

Polymeric membranes when exposed to certain solvents tend to swell overtime. This behavior is termed as plasticization. In the aboveexperiments, as the membrane became plasticized it loss the ability todiscriminate between ethanol and water. This led to more ethanol fluxthrough the hydrophilic membrane,and as a result, the selectivity ofwater over ethanol decreases over the course of the experiment. Theethanol flux should increase with increase in the fugacity orconcentration. However, a reverse trend is observed (FIG. 11A) where theethanol flux decreases with the increase in fugacity (or the feedconcentration) of ethanol. Therefore, it is plausible to conclude thatthe ethanol flux is influenced by another factor; most probably by theplasticization of the membrane due to the water present in feed. Thisexplanation is verified with the dependence of ethanol flux on the feedwater concentration or fugacity (FIG. 11B). The increase in ethanol fluxwith water concentration is a direct effect of plasticization of the PVAmembrane by water. The plasticization effect is confirmed further as theconcentration of water in the feed increases (FIG. 12), the selectivityof water/ethanol drops with the corresponding increase in ethanol flux(FIG. 11B). For the different runs performed the selectivity ofwater/ethanol drops from 450 to 200 depending on the waterconcentration.

A pervaporation system has been demonstrated that can dehydrate alcoholcompositions for use in hydrocarbon fuels. Use of a pervaporation systemwill reduce CO₂ emissions and decrease the carbon footprint forproducing renewable fuels. This improves the advanced cellulosic fuelproduction process by decreasing CO₂ production for renewable fuelsproduced using this system. Decreasing CO₂ is essential to achieve theappropriate carbon reduction for an advanced cellulosic renewable fuel.

Example 3 Production of Advanced Cellulosic Renewable Fuels

A complete system and method of producing advanced cellulosic renewablefuels has been developed that uses an biomass source with high levels ofoxygenate and converts the oxygenated biomass to ethanol and blendedethanol renewable gasoline fuels. Oxygenates, including solublecarbohydrates, organic acids, polyols, and alcohols are produced frombiomass through a variety of reactions including acid hydrolysis,pyrolysis, fermentation and other conventional biomass conversions. Theoxygen rich aqueous solutions are difficult to process because of thecorrosive nature of oxygenate containing solutions and subsequent cokingpropensity of these mixtures inside reactors. The system developed(FIG. 1) produces gasoline range fuels and fuel grade alcohols ready toblend as advanced cellulosic renewable fuels that are fungible withcurrent gasoline products. This method demonstrates the production of aneat fuel product blend that can be synthesized from 100% renewablematerial and integrated without any deleterious effects on the currenthydrocarbon transportation pipeline infrastructure and vehiclepowertrains.

In one embodiment (FIG. 1), incoming dilute aqueous oxygenate solutionsare separated into an organic acid fraction and a polyol fraction usingone or more ionic separations (ISEP) as required by the composition ofthe incoming oxygenate solution. The polyol fraction is transferred to atraditional hydrotreating (HT) reactor. The hydrotreating (HT) reactorproduces various alkanes, water, light hydrocarbon byproducts andintermediates. The alkanes produced by from hydrotreating can beisomerized in to various fuel range products in an isomerizationreactor. The organic acids and hydrogen are fed to a hydrodeoxygenation(HDO) reactor to produce various alcohols from the mixed organic acids.The aqueous alcohol solutions produced are separated using coldseparation into an aqueous fraction and an alcohol fraction. The alcoholfraction containing between 50 and 99% wt % alcohol are dehydrated usingpervaporation to produce fuel grade alcohol with less than 500 ppmwater. The dehydrated alocohol is blended with the isomerized fuelproducts to produce commercial grade E85 fuel with up to 85% alcohol,E10 fuel with up to 10% alcohol, E20 with up to 20% alcohol and premiumfuel with an octane rating between 97 and 103 octane.

In another embodiment (FIG. 2), pyrolysis oil containing organic acidsincluding acetic acid and polyols including sorbitol are upgraded toadvanced cellulosic renewable fuels. An aqueous pyrolysis oil feedstockis separated into an acetic acid fraction and a sorbitol fractionthrough ionic separation. The sorbitol fraction is converted withnaphtha and hydrogen to produce n-hexane through hydrodesulferization.Hexane is separated from water and H₂S to produce dry hexane. The dryhexane is isomerized to produce any number of fuel range hydrocarbonsincluding aromatics, paraffins, naphthas, and the like, dependent uponthe temperatures and length of isomeriziation reaction. A portion of thehexane is mixed with the acetic acid solution and hydrogen for HDO.Ethanol and water from HDO are cold separated to remove water. Producedethanol between 50 and 90% wt % ethanol is dehydrated by one or morepervaporation steps to produce ethanol with less than 500 ppm water.Ethanol may contain less than 200 ppm water after pervaporation. In oneembodiment, ethanol contains less than 100 ppm water. Ethanol and fuelrange hydrocarbons are blended to produce E85, E20, E10, and/or premiumgasoline range fuel products.

Advanced cellulosic renewable fuels are produced from biomass oxygenatesolutions. The system described produces both renewable alcohols andrenewable fuel range hydrocarbons that can be blended with or withoutnon-renewable hydrocarbons. This demonstrates a 100% renewable fuelproduct with very low CO₂ production. The renewable fuel product can beincorporated into existing fuel systems without modification.

In closing, it should be noted that the discussion of any reference isnot an admission that it is prior art to the present invention,especially any reference that may have a publication date after thepriority date of this application. At the same time, each and everyclaim below is hereby incorporated into this detailed description orspecification as a additional embodiments of the present invention.

Although the systems and processes described herein have been describedin detail, it should be understood that various changes, substitutions,and alterations can be made without departing from the spirit and scopeof the invention as defined by the following claims. Those skilled inthe art may be able to study the preferred embodiments and identifyother ways to practice the invention that are not exactly as describedherein. It is the intent of the inventors that variations andequivalents of the invention are within the scope of the claims whilethe description, abstract and drawings are not to be used to limit thescope of the invention. The invention is specifically intended to be asbroad as the claims below and their equivalents.

REFERENCES

All of the references cited herein are expressly incorporated byreference. The discussion of any reference is not an admission that itis prior art to the present invention, especially any reference that mayhave a publication data after the priority date of this application.Incorporated references are listed again here for convenience:

-   1. U.S. Pat. No. 1,302,011, Christiansen, (1919).-   2. U.S. Pat. No. 1,605,093, Bouvier and Blanc,(1926).-   3. U.S. Pat. No. 1,971,742, Berisch, H., (1934).-   4. U.S. Pat. No. 2,079,414, Lazier, (1937).-   5. U.S. Pat. No. 2,091,800, Adkins, et al., (1937).-   6. U.S. Pat. No. 2,093,159, Schmidt,. (1937).-   7. U.S. Pat. No. 2,322,095, Schmidt, (1943).-   8. U.S. Pat. No. 2,322,096, Schmidt, (1943).-   9. U.S. Pat. No. 2,322,097, Schmidt, (1943).-   10. U.S. Pat. No. 2,549,416, Brooks, (1951).-   11. U.S. Pat. No. 2,607,807, Ford, (1952).-   12. U.S. Pat. No. 2,782,243, Hess and Schulz, (1957).-   13. U.S. Pat. No. 3,197,418, Maebashi and Yamo, (1965).-   14. U.S. Pat. No. 3,361,832, Pine and Ellert, (1968).-   15. U.S. Pat. No. 3,363,009, Schuman, (1968).-   16. U.S. Pat. No. 3,478,112, Adam, et al., (1969).-   17. U.S. Pat. No. 4,113,662, Wall, (1978).-   18. U.S. Pat. No. 4,149,021, Wall, (1979).-   19. U.S. Pat. No. 4,220,803, Marcinkowsky and Henry, (1980).-   20. U.S. Pat. No. 4,282,323, Yates, (1981).-   21. U.S. Pat. No. 4,283,581, Wilkes, (1981).-   22. U.S. Pat. No. 4,359,404, Grey and Pez, (1982).-   23. U.S. Pat. No. 4,398,039, Pesa, et al., (1983).-   24. U.S. Pat. No. 4,421,939, Kiff and Schreck, (1983).-   25. U.S. Pat. No. 4,443,639, Pesa, et al., (1984).-   26. U.S. Pat. No. 4,456,775, Travers, et al., (1984).-   27. U.S. Pat. No. 4,517,391, Ludwig, et al., (1985).-   28. U.S. Pat. No. 4,611,085, Kitson, (1986).-   29. U.S. Pat. No. 4,628,130, Bournonville, et al., (1986).-   30. U.S. Pat. No. 4,762,817, Logsdon, et al., (1988).-   31. U.S. Pat. No. 4,777,303, Kitson and P.S. Williams,. 1988.-   32. U.S. Pat. No. 4,804,791, Kitson and Williams, (1989).-   33. U.S. Pat. No. 4,826,795, Kitson and Williams, (1989).-   34. U.S. Pat. No. 4,918,248, Hattori, et al., (1990).-   35. U.S. Pat. No. 4,929,777, Irick, et al., (1990).-   36. U.S. Pat. No. 4,973,717, Williams, (1990).-   37. U.S. Pat. No. 4,985,572, Kitson and Williams, (1991).-   38. U.S. Pat. No. 5,008,235, Wegman and Bryant, (1991).-   39. U.S. Pat. No. 5,142,067, Wegman and Bryant, (1992.-   40. U.S. Pat. No. 5,149,680, Kitson and Williams, (1990).-   41. U.S. Pat. No. 5,155,086, Thakur, et al., (1992).-   42. U.S. Pat. No. 5,345,005, Thakur, et al., (1994).-   43. U.S. Pat. No. 5,387,753, Scarlett, et al., (1995).-   44. U.S. Pat. No. 5,403,962, Schneider, et al., (1995).-   45. U.S. Pat. No. 5,478,952, Schwartz, (1995).-   46. U.S. Pat. No. 5,475,159, Singleton and Murray, (1995).-   47. U.S. Pat. No. 5,959,167, W09910450, Shabtai, et al., (1999).-   48. U.S. Pat. No. 6,008,384, Bockrath, et al., (1999).-   49. U.S. Pat. No. 6,054,627, Thakur, et al., (2000).-   50. U.S. Pat. No. 6,140,545, Merger, et al., (2000).-   51. U.S. Pat. No. 6,403,844, Zhang, et al., (2002).-   52. U.S. Pat. No. 6,455,464, Chen, (2002).-   53. U.S. Pat. No. 6,509,180, Verser and Eggeman, (2003).-   54. U.S. Pat. No. 6,765,118, Fischer, et al., (2004).-   55. U.S. Pat. No. 7,119,237, Prinz, et al., (2006).-   56. U.S. Pat. No. 7,351,559, Verser and Eggeman, (2008).-   57. U.S. Pat. No. 7,578,927, US2008053870, WO2008027699, Marker and    Petri, “Gasoline and Diesel Production from Pyrolytic Lignin    Produced from Pyrolysis of Cellulosic Waste” (2008).-   58. US2008050792, WO2006119357, Zmierczak and Miller, “Processes for    Catalytic Conversion of Lignin To Liquid Bio-Fuels And Novel    Bio-Fuels” (2006)-   59. US2008092435, WO2008051984, Bzdek and Pellegrino, “Methods of    Purifying Biodiesel Fuels” (2008)-   60. WO2008113492, Baldiraghi, et al., “Hydrocarbon Composition    Useful as a Fuel and Fuel Oil Containing a Petroleum Component and a    Component of a Biological Origin” (2008)-   61. WO2010145901, Vandezande, et al., “Thin Film Pervaporation    Membranes.” (2010).-   62. EP0175558, Moy, (1986).-   63. EP0198681, Kitson and Williams, (1986).-   64. EP0285420, Kitson and Sefton, (1988).-   65. EP0953560, Tustin, e al., (1999).-   66. Baker, “Pervaporation, in Membrane technology and applications.”    Wiley. p. 355-392 (2004).-   67. Benaissa, H., et al., “Heteropoly Compounds as Catalysts for    Hydrogenation of Propanoic Acid.” J. Catalysis 253:244-252 (2008).-   68. Holman and Gajda, “Analysis of experimental data, in    Experimental methods for engineers.” McGraw-Hill New York. p. 46-94    (1994).-   69. Kleinert, et al., “Optimizing solvolysis conditions for    integrated depolymerisation and hydrodeoxygenation of lignin to    produce liquid biofuels.” J. Analytical and Applied Pyrolysis    85:108-117 (2009).-   70. Mulder and Smolders, “On the mechanism of separation of    ethanol/water mixtures by pervaporation. I: Calculations of    concentration profiles.” J. Membrane Sci., 17:289-307 (1984).-   71. Nagayama, et al., “Direct Hydrogenation of Carboxylic Acids    Corresponding Aldehydes Catalyzed by Palladium Complexes.” Bull.    Chem. Soc. Jpn., 74:1803-15 (2001).-   72. Natal Santiago, et al., “Catalytic Reduction of Acetic Acid,    Methyl Acetate, Ethyl Acetate over Silica-Supported Copper.” Journal    of Catalysis, 193:16-28 (2000).-   73. Pan and Habgood, “Gas separation by permeation Part II: Effect    of permeate pressure drop and choice of permeate pressure.”    Canadian J. Chem. Eng., 56:210-217 (2009).-   74. Peng, et al., “Recent advances in VOCs removal from water by    pervaporation.” J. Hazardous Materials, 98:69-90 (2003).-   75. Pestman, et al., “Selective Hydrogenation of Acetic Acid Towards    Acetaldehyde.” J. Royal Netherlands Chem. Soc., 113:426-30 (1994).-   76. Pestman, et al., Reactions of Carboxylic Acids on Oxides: 1.    Selective Hydrogenation of Acetic Acid to Acetaldehyde. J.    Catalysis, 168:255 - 264 (1997).-   77. Pestman, et al., “Identification of the Active Sites in the    Selective Hydrogenation of Acetic Acid to Acetaldehyde on Iron Oxide    Catalysts.” J. Catalysis,. 174:142-52 (1998).-   78. Rachmady and Vannice, “Acetic Acid Hydrogenation over Supported    Platinum Catalysts.” J. Catalysis, 192:322-34 (2000).-   79. Rachmady and Vannice, “Acetic Acid Reduction to Acetaldehyde    over Iron Catalysts.” J. Catalysis, 208:158-69 (2002).-   80. Rachmady and Vannice, “Acetic Acid Reduction by H₂ on Bimetallic    PtFe Catalysts.” J. Catalysis, 209:87-98 (2002).-   81. Ribeiro and Borges, “Using pervaporation data in the calculation    of vapour permeation hollow-fibre modules for aroma recovery.”    Brazilian J. Chem. Eng., 21:629-640 (2004).-   82. Ribeiro, et al., “A combined gas-stripping vapour permeation    process for aroma recovery.” J. Membrane Science 238:9-19 (2004).-   83. Shih and Keng, “Kinetics of the Ruthenium-Catalyzed    Hydrogenation of Acetic Acid to Ethanol.” J. Chin. Chem. Soc.,    32:29-34 (1985).-   84. Smith, et al., “Introduction to chemical engineering    thermodynamics.” McGraw-Hill Science/Engineering/Math (2005).-   85. Tahara, et al., “Liquid-Phase Hydrogenation of Carboxylic Acid    on Supported Bimetallic Ru-Sn-Alumina Catalysts.” Appl. Catal.    A:General, 154:75-86 (1997).-   86. Toba, et al., “Synthesis of Alcohols and Dials by Hydrogenation    of Carboxylic Acids and Esters over Ru-Sn-Al₂O₃ Catalysts.” Appl.    Catal. A:General, 189:243-50 (1999).-   87. Vane, “A review of pervaporation for product recovery from    biomass fermentation processes.” J. Chem. Tech. Biotech. 80:603-629    (2005).-   88. Yokoyama and Yamagata, “Hydrogenation of Carboxylic Acids to the    Corresponding Aldehydes.” Appl. Catal. A:General, 221:227-39 (2001).-   89. Yokoyama and Fujita, “Hydrogenation of Aliphatic Carboxylic    Acids to Corresponding Aldehydes over Cr203-based Catalysts.” Appl.    Catal. A:General, 276:179-85 (2004).

The invention claimed is:
 1. A method for producing a renewable gasolinefrom cellulosic biomass comprising: a) separating a cellulosicfeedstream in an ionic separator to generate a polyol stream comprisingat least one of sugars and polyols and an organic stream comprising oneor more organic acids and water; b) generating hydrocarbons comprisingalkanes from the polyol stream in a hydrotreating reactor and convertingat least a portion of the hydrocarbons to isomerized gasoline rangehydrocarbons in an isomerization reactor c) generating alcohol from theorganic stream, at least a portion of the hydrocarbons from thehydrotreating reactor and hydrogen in a hydrodeoxygenation reactor d)separating the alcohol, water, and hydrogen in a cold separator, andremoving water using a membrane separator; and e) producing one or moreproduct renewable gasoline streams comprising the alcohols, at least aportion of the hydrocarbons from the hydrotreating reactor and theisomerized gasoline range hydrocarbons.
 2. The method of claim 1,wherein said hydrodeoxygenation reactor comprises a catalyst selectedfrom the group consisting of CuO, ZnO, Fe2O3, CuO/ZnO, CuO/Fe2O3,ZnO/Fe2O3, CuO/ZnO/Fe2O3, CuO/ZnO/Al2O3, CuO/Al2O3/SiO2,CuO/Fe2O3/Al2O3/SiO2, and combinations thereof.
 3. The method of claim1, wherein said membrane separator comprises a membrane selected fromthe group consisting of hydrophilic, hydrophobic, organophillic,polydimethylsiloxane (PDMS), polyvinyl alcohol (PVA), polyimide,ceramic, zeolite, amorphous silica, hybrid membranes, and combinationsthereof.